Phytoremediation of textile effluents containing azo dye by using Phragmites australis in a vertical flow intermittent feeding constructed wetland

An azo dye, acid orange 7 (AO7), was selected to study the role of Phragmites australis (P. australis) peroxidases (POD) activity in its degradation in a vertical flow constructed wetland (VFCW). Crude plant extract was found to degrade AO7 and its aromatic amines, after 120 h in contact with H₂O₂, and removals of were obtained for 40 mg_AO7 l⁻¹ ().The VFCW was found to be suitable to treat an effluent containing an azo dye. For influent concentrations of 130 mg_AO7 l⁻¹ POD activity increased 2.1-, 4.3- and 12.9-fold for leaves, stems and roots, respectively. At 700 mg_AO7 l⁻¹, inhibition of POD activity occurred immediately, but it returned to the previous levels after only 2 days. An AO7 organic load of 21 up to 105 g COD m² day⁻¹, revealed non-toxicity, being expectable to achieve removals of 11 up to 67 g COD m² day⁻¹. Both [AO7] and TOC removal efficiencies were found to be similar (approximately 70%), which is indicative of AO7 mineralization. A 3 h cycle was found to be sufficient to degrade AO7 and a system buffering capacity from 5 to 25 min cycle⁻¹ was demonstrated by flooding level control.     

Estimate of life-cycle greenhouse gas emissions from a vertical subsurface flow constructed wetland and conventional wastewater treatment plants: A case study in China

This study aims to estimate the three greenhouse gas (GHG) emissions (i.e. CO₂, CH₄, N₂O) from a vertical subsurface flow constructed wetland (VSSF CW, 1000 m²) and a cluster of conventional wastewater treatment plants (WWTPs) in the city of Changzhou, China. The two estimated emissions are set up for comparison. The results show that the WWTP system emits 7.3 kg CO₂-eq to remove 1 kg BOD in the studied life cycle, while the VSSF system only emits 3.18 kg CO₂-eq, which is only half of the amount given off by the WWTP system. Especially at the treatment stage, the WWTP system's GHG emissions are almost 7 times higher than the VSSF system's. N₂O emissions in both systems are only a minor fraction of the total emissions. Therefore, this study has concluded that the VSSF system is an effective option for GHG emissions mitigation in the wastewater sector. The study further suggests that developing countries like China should extensively build up VSSF systems for decentralized wastewater treatment, which could also potentially reduce GHG emissions by 8-17 million ton CO₂-eq per year compared with the centralized scenario.     

Evaluation of a lab-scale tidal flow constructed wetland performance: Oxygen transfer capacity, organic matter and ammonium removal

Oxygen transfer capacity and removal of ammonium and organic matter were investigated in this study to evaluate the performance of a lab-scale tidal flow constructed wetland. Average oxygen supply under tidal operation (350 g m⁻² d⁻¹) was much higher than in conventional constructed wetlands (<100 g m⁻² d⁻¹), resulting in enhanced removal of BOD₅ and NH₄⁺. Theoretical oxygen demand from BOD₅ removal and nitrification was approximately matched by the measured oxygen supply, which indicated aerobic consumption of BOD₅ and NH₄⁺ under tidal operation. When BOD₅ removal increased from 148 g m⁻² d⁻¹ to 294 g m⁻² d⁻¹, neither exhausted oxygen from the aggregate matrix during feeding period (111 g m⁻² d⁻¹) nor effluent dissolved oxygen (DO) concentration (2.8 mg/L) changed significantly, demonstrating that the oxygen transfer potential of the treatment system had not been exceeded. However, even though DO had not been exhausted, inhibition of nitrification was observed under high BOD loading. The loss of nitrification was attributed to excessive heterotrophic biofilm growth believed to induce oxygen transfer limitations or oxygen competition in thickened biofilms.     

Efficiency of two-stage combinations of subsurface vertical down-flow and up-flow constructed wetland systems for treating variation in influent C/N ratios of domestic wastewater

The performance and temporal variation of four hybrid, intermittent loading, pilot-scale vertical flow constructed wetlands (VFCWs) were tested for treating domestic wastewater of three different C/N ratios (2.5:1, 5:1, and 10:1, respectively). Two hybrid systems each consisted of the two identical VFCWs in-series, with up-up or down-down flow. The other two hybrid systems consisted of the first VFCWs (up or down flow) followed by a second VFCWs (down or up flow, respectively). The effects of combination mode, season, load level, and interactions on nutrient removal were studied in synthetic wastewater in the two-stage VFCW systems. With varying C/N ratios for influent water (from 2.5:1, 5:1 to 10:1) average removal efficiencies for the two-bed two-stage systems were as follows: COD 73-93%, TN 46-87%, TP 75-90%, and TOC 40-66%, respectively. All two-bed hybrid VFCWs were efficient in removing organics and total phosphorus, and reached the highest removal rates when the C/N ratios were 10 and 5, respectively. The hybrid systems for different flow direction beds had significantly higher performance (P < 0.05) during the wetlands operational period. Compared to the four types of hybrid VFCWs, the two-stage combination with different flow directions achieved significantly higher TN and TOC reductions (P < 0.05). The highest total nitrogen (P < 0.05) and total phosphorus reductions in down-up flow VFCWs were observed at C/N 5:1. However, for organic matter and total organic carbon, the highest COD and TOC removal rates occurred when C/N ratios were 5-10 for the down-up flow VFCWs. With appropriate control of combined mechanisms in series, the concentrations of carbon and nitrogen sources in the influent can achieve the optimal effects of nutrient removal.     

Photooxidation of the cytochrome b-559 in the presence of various substituted 2-anilinothiophenes and of some other compounds,in Chlamydomonas reinhardtii

Five substituted 2-anilinothiophenes and two substituted carbonylcyanide-phenylhydrazones were comparatively studied with respect to their capacities for inducing photooxidation of the cytochrome b-559 in chloroplast fragments and in whole cells of Chlamydomonas reinhardtii (wild type and P-700-lacking mutant Fl 5). In addition, some other compounds: antimycin A, picric acid, tetraphenylboron and NH₄Cl were also tested.Cytochrome b-559 photooxidations were clearly observed in the presence of 2-(3-chloro-4-trifluoromethyl)anilino-3,5-dinitrothiophene (ANT 2p), 2-(3,4,5-trichloro)anilino-3,5-dinitrothiophene (ANT 2s), 2-(4-chloro)anilino-3,5-dinitrothiophene and, with greater amplitudes, in the presence of carbonylcyanide-p-trifluoromethoxyphenylhydrazone and carbonylcyanide-m-chlorophenylhydrazone, both in whole cells and in chloroplast fragments. Picric acid, antimycin A and tetraphenylboron were also able to induce cytochrome b-559 photooxidation in chloroplast fragments, but not in whole cells. In the wild type, the highest photoinduced redox changes were 1.1 (carbonylcyanide-p-trifluoromethoxyphenylhydrazone, carbonylcyanide-m-chlorophenylhydrazone) and 0.6 (ANT 2p, ANT 2s) μmol of oxidized cytochrome b-559/1 mmol of chlorophyll, corresponding to 40% and 23% of the redox changes which could be induced chemically. All these cytochrome b-559 photooxidations, the greater part of which was inhibited by 3-(3,4-dichlorophenyl)-1,1-dimethylurea and occurred in the mutant Fl 5, appeared to be mainly Photosystem II-dependent reactions. But 3-(3,4-dichlorophenyl)-1,1-dimethylureainsensitive Photosystem I-dependent photooxidations of cytochrome b-559 occurred also in the wild type. On the other hand, 2-(4-dimethylamine)-anilino-3,5-dinitrothiophene, 2-N-methyl-(3-chloro-4-trifluoromethyl)anilino3,5-dinitrothiophene and NH₄Cl did not induce any cytochrome b-559 photooxidation.These results were discussed taking in consideration the nature of the molecular substitutions of the various tested substances and their respective acceleration of the deactivation reactions of the water-splitting enzyme system Y of photosynthesis capacities which had been defined elsewhere by Renger (Renger, G. (1972) Biochim. Biophys. Acta 256, 428–439) for spinach chloroplasts. Like the acceleration of the deactivation reactions of the water-splitting enzyme system Y effect, the capacity for inducing the cytochrome b-559 photooxidation appeared dependent on the acidity of the NH group and on the number of halogenous substituents in the aromatic ring of the molecule. The greatest action towards cytochrome b-559 photooxidation was obtained with the most active acceleration of the deactivation reactions of the water-splitting enzyme system Y agents: carbonylcyanide-p-trifluoromethoxyphenylhydrazone, ANT 2p and ANT 2s.